首页 | 本学科首页   官方微博 | 高级检索  
     

高通量固相萃取-超高效液相色谱-串联质谱法测定人尿中8种环境酚类内分泌干扰物
引用本文:林潇,邱天,张续,胡小键,杨艳伟,朱英. 高通量固相萃取-超高效液相色谱-串联质谱法测定人尿中8种环境酚类内分泌干扰物[J]. 色谱, 2020, 38(12): 1456-1464. DOI: 10.3724/SP.J.1123.2020.07021
作者姓名:林潇  邱天  张续  胡小键  杨艳伟  朱英
作者单位:中国疾病预防控制中心环境与人群健康重点实验室, 中国疾病预防控制中心环境与健康相关产品安全所, 北京 100021
摘    要:建立了人尿中8种环境酚类化合物的96孔板固相萃取-超高效液相色谱-串联质谱(96-well SPE LC-MS/MS)检测方法,其中包括7种双酚类化合物和三氯生。尿样解冻到室温,经β-葡萄糖醛酸苷肽酶/芳基磺酸酯酶37℃过夜酶解。实验比较了3种96孔板固相萃取柱和不同淋洗条件对人尿样的净化效果和目标化合物的回收率。结果显示,采用Oasis HLB 96孔板(60 mg)对样品进行萃取和用30%(v/v)乙腈水溶液进行淋洗净化的纯化效果最好。纯化后目标物用甲醇溶液洗脱,经氮气吹干,用0.5 mL甲醇-水(1∶1, v/v)溶液定容,目标化合物用UPLC-MS/MS进行检测。比较了2种分析柱(C18和T3分析柱)以及不同的有机流动相对分离样品中目标物的影响。结果显示,以BEH C18(100 mm×2.1 mm, 1.7μm)作为分析柱,乙腈/水作为流动相,以流速0.3 mL/min梯度洗脱时,目标物的分离效果最好。质谱条件选择串联质谱负离子电喷雾(ESI-)多反应监测模式(MRM)进行检测。对样品的基质效应进行评估发现,双...

关 键 词:固相萃取  超高效液相色谱-串联质谱  环境酚类化合物  内分泌干扰物  尿样  96孔板
收稿时间:2020-07-22

Determination of eight environmental phenols in human urine samples by high-throughput solid-phase extraction-ultra-performance liquid chromatography-tandem mass spectrometry
LIN Xiao,QIU Tian,ZHANG Xu,HU Xiaojian,YANG Yanwei,ZHU Ying. Determination of eight environmental phenols in human urine samples by high-throughput solid-phase extraction-ultra-performance liquid chromatography-tandem mass spectrometry[J]. Chinese journal of chromatography, 2020, 38(12): 1456-1464. DOI: 10.3724/SP.J.1123.2020.07021
Authors:LIN Xiao  QIU Tian  ZHANG Xu  HU Xiaojian  YANG Yanwei  ZHU Ying
Affiliation:China CDC Key Laboratory of Environment and Population Health, National Institute of Environmental Health, Chinese Center for Disease Control and Prevention, Beijing 100021, China
Abstract:A method combining 96-well plate solid-phase extraction with ultra-performance liquid chromatography-tandem mass spectrometry (96-well SPE LC-MS/MS) was developed for the simultaneous determination of eight environmental phenols in urine samples. The samples included seven bisphenol compounds and triclosan. The urine samples were thawed to room temperature, and the target analytes were deconjugated by β-glucuronidase/aryl-sulfatase in ammonium acetate buffer solution at 37 ℃ overnight. Then, the effects of three kinds of 96-well solid-phase extraction plates and different elution conditions on the purification of the urine samples and the environmental phenol recoveries were compared. The best purification effect was achieved on Oasis HLB 96-well plate (60 mg) solid phase extraction, using 30% (v/v) acetonitrile aqueous solution as the rinse solution. The target analytes were then eluted by methanol solution and evaporated to dryness using a nitrogen blower. After reconstruction with 0.5 mL methanol/water (1∶1, v/v) solution, the target compounds were detected by UPLC-MS/MS. To achieve better chromatographic separation, two kinds of analytical columns (C18 and T3) and different types of mobile phases (methanol and acetonitrile as the organic phase) were also compared. The best chromatographic effect was achieved when the treated samples were separated on a C18 column (100 mm×2.1 mm, 1.7 μm) using acetonitrile/water as the mobile phase at a flow rate of 0.3 mL/min. Mass spectra were recorded by negative electrospray ionization under the multiple reaction monitoring (MRM) mode. The sample matrix effect was also evaluated. The absolute matrix effects of bisphenol A, bisphenol F, bisphenol S, bisphenol B, and bisphenol AF were in the range of 3.47% to 15.32%. Since the above mentioned matrix effect was weak, there was no need for compensation measures. On the contrary, tetrachlorobisphenol A, tetrabromobisphenol A, and triclosan showed an absolute matrix effect of 49.58% (moderate), 71.99% (strong), and 86.93% (strong), thus necessitating compensation measures. Therefore, this strategy uses a one-to-one corresponding isotope internal standard method to offset the matrix effect. Six different urine samples were used to evaluate the relative matrix effect. The relative standard deviations (RSDs) of the eight corresponding internal standard peak areas were 3.63%-9.06%, indicating that the relative matrix effect was stable. Under the optimized conditions, linearity ranges were 0.50-50 μg/L for bisphenol A and bisphenol AF; 0.05-50 μg/L for tetrachlorobisphenol A and bisphenol S; 0.01-50 μg/L for bisphenol F and tetrabromobisphenol A; 1.00-50 μg/L for bisphenol B; and 5.00-200 μg/L for triclosan. The correlation coefficients were all greater than 0.9995. At spiked levels of 2.5, 5, and 25 μg/L, the average recovery ratios of the eight target analytes were 81.01%-118.84%, while the intra-day and inter-day precisions were 0.38%-19.41% and 2.54%-17.83%, respectively. The limits of detection (LOD) were 0.002-1.09 μg/L, and the limits of quantitation (LOQ) were 0.007-3.63 μg/L. This method was successfully applied to the determination of the eight environmental phenols in 64 urine samples collected from Beijing area between 2019 and 2020. All the target environmental phenols were detected, except for bisphenol B and bisphenol AF. Bisphenol A and bisphenol S showed the highest detection rates of 100% and 96.9%, respectively. The detection rates of triclosan, tetrabromobisphenol A, tetrachlorobisphenol A, and bisphenol F were 57.8%, 46.9%, 23.4%, and 21.9%, respectively. The medium values of urinary concentration followed the order 1.44 μg/L(triclosan), 0.69 μg/L(bisphenol A), 0.086 μg/L (bisphenol S), 0.0032 μg/L (tetrabromobisphenol A), 0.00050 μg/L (tetrachlorobisphenol A), 0.00 μg/L (bisphenol F, bisphenol B, and bisphenol AF). The aforementioned results imply that the widespread environmental phenolic exposure of Beijing residents is worthy of attention. Compared with traditional solid-phase extraction methods, the method reported in this paper is time-saving, effective, and suitable for the simultaneous analysis of large quantities of samples; moreover, the small sample and organic solvent consumption make this method more environment- and operator-friendly.
Keywords:solid phase extraction (SPE)  ultra-performance liquid chromatography-tandem mass spectrometry (UPLC-MS/MS)  environmental phenols  endocrine disrupters  urine sample  96-well plate  
点击此处可从《色谱》浏览原始摘要信息
点击此处可从《色谱》下载全文
设为首页 | 免责声明 | 关于勤云 | 加入收藏

Copyright©北京勤云科技发展有限公司  京ICP备09084417号